Taking of Marine Mammals Incidental to Commercial Fishing Operations; Atlantic Pelagic Longline Take Reduction Plan, 35623-35631 [E8-14274]
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Federal Register / Vol. 73, No. 122 / Tuesday, June 24, 2008 / Proposed Rules
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Issued on: June 11, 2008.
Stephen P. Wood,
Assistant Chief Counsel for Vehicle Safety,
Standards and Harmonization.
[FR Doc. E8–13592 Filed 6–23–08; 8:45 am]
BILLING CODE 4910–59–P
DEPARTMENT OF COMMERCE
National Oceanic and Atmospheric
Administration
50 CFR Part 229
[Docket No. 070717352–8511–0]
RIN 0648–AV65
Taking of Marine Mammals Incidental
to Commercial Fishing Operations;
Atlantic Pelagic Longline Take
Reduction Plan
National Marine Fisheries
Service (NMFS), National Oceanic and
Atmospheric Administration (NOAA),
Commerce.
ACTION: Proposed rule; notice of
availability of draft take reduction plan;
request for comments.
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AGENCY:
SUMMARY: The National Marine
Fisheries Service (NMFS) announces the
initial determination that the pelagic
longline fishery has a high level of
mortality and serious injury across a
number of marine mammal stocks, and
proposes regulations to implement the
Atlantic Pelagic Longline Take
Reduction Plan (PLTRP) to reduce
serious injuries and mortalities of pilot
whales and Risso’s dolphins in the
Atlantic pelagic longline fishery. The
PLTRP is based on consensus
recommendations submitted by the
Atlantic Pelagic Longline Take
Reduction Team (PLTRT). This action is
necessary because current serious injury
and mortality rates of pilot whales and
Risso’s dolphins incidental to the
Atlantic pelagic longline component of
a Category I fishery are above
insignificant levels approaching a zero
mortality and serious injury rate (zero
mortality rate goal, or ZMRG), and
therefore, inconsistent with the longterm goal of the Marine Mammal
Protection Act (MMPA). The PLTRP is
intended to meet the statutory mandates
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and requirements of the MMPA through
both regulatory and non-regulatory
measures, including a special research
area, gear modifications, outreach
material, observer coverage, and
captains’ communications.
DATES: Written comments on the
proposed rule must be received no later
than 5 p.m. eastern time on September
22, 2008.
ADDRESSES: You may submit comments,
identified by the Regulatory Information
Number (RIN) 0648–AV65, by any of the
following methods:
• Electronic Submissions: Submit all
electronic public comments via the
Federal eRulemaking Portal https://
www.regulations.gov.
• Facsimile (fax): 727 824–5309, Attn:
Assistant Regional Administrator,
Protected Resources.
• Mail: Assistant Regional
Administrator for Protected Resources,
NMFS, 263 13th Avenue South, St.
Petersburg, FL 33701.
Instructions: All comments received
are a part of the public record and will
generally be posted to https://
www.regulations.gov without change.
All Personal Identifying Information (for
example, name, address, etc.)
voluntarily submitted by the commenter
may be publicly accessible. Do not
submit Confidential Business
Information or otherwise sensitive or
protected information.
NMFS will accept anonymous
comments. Attachments to electronic
comments will be accepted in Microsoft
Word, Excel, WordPerfect, or Adobe
PDF file formats only.
This proposed rule, references, and
background documents for the PLTRP
can be downloaded from the Take
Reduction web site at https://
www.nmfs.noaa.gov/pr/interactions/trt/
teams.htm#pl-trt.htm and the NMFS
Southeast Regional Office website at
https://sero.nmfs.noaa.gov/pr/pr.htm.
FOR FURTHER INFORMATION CONTACT:
Laura Engleby or Jennifer Lee, NMFS,
Southeast Region, 727–824–5312, or
Kristy Long, NMFS, Office of Protected
Resources, 301–713–2322. Individuals
who use telecommunications devices
for the deaf (TDD) may call the Federal
Information Relay Service at 1–800–
877–8339 between 8 a.m. and 4 p.m.
eastern time, Monday through Friday,
excluding Federal holidays.
SUPPLEMENTARY INFORMATION:
Bycatch Reduction Requirements in the
MMPA
Section 118(f)(1) of the MMPA
requires NMFS to develop and
implement take reduction plans to assist
in the recovery or prevent the depletion
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of each strategic marine mammal stock
that interacts with Category I and II
fisheries. It also provides NMFS
discretion to develop and implement a
take reduction plan for any other marine
mammal stocks that interact with a
Category I fishery, which the agency
determines, after notice and opportunity
for public comment, has a high level of
mortality and serious injury across a
number of such marine mammal stocks.
The MMPA defines a strategic stock
as a marine mammal stock: (1) for which
the level of direct human-caused
mortality exceeds the potential
biological removal (PBR) level; (2)
which is declining and is likely to be
listed under the Endangered Species Act
(ESA) in the foreseeable future; or (3)
which is listed as threatened or
endangered under the ESA or as a
depleted species under the MMPA (16
U.S.C. 1362(2)). PBR is the maximum
number of animals, not including
natural mortalities, that can be removed
annually from a stock, while allowing
that stock to reach or maintain its
optimum sustainable population level.
Category I or II fisheries are fisheries
that, respectively, have frequent or
occasional incidental mortality and
serious injury of marine mammals.
The immediate goal of a take
reduction plan for a strategic stock is to
reduce, within six months of its
implementation, the incidental serious
injury or mortality of marine mammals
from commercial fishing to levels less
than PBR. The long-term goal is to
reduce, within five years of its
implementation, the incidental serious
injury and mortality of marine mammals
from commercial fishing operations to
insignificant levels approaching a zero
serious injury and mortality rate, taking
into account the economics of the
fishery, the availability of existing
technology, and existing state or
regional fishery management plans. The
insignificance threshold, or upper limit
of annual incidental mortality and
serious injury of marine mammal stocks
by commercial fisheries that can be
considered insignificant levels
approaching a zero mortality and
serious injury rate, has been defined at
50 CFR 229.2 as 10 percent of the PBR
for a stock of marine mammals.
Impetus and Scope of the Plan
The impetus for this plan was a 2003
settlement agreement between NMFS
and the Center for Biological Diversity
(CBD), that required the convening of a
Take Reduction Team (the PLTRT)
under the MMPA by June 30, 2005, to
address serious injury and mortality of
short- and long-finned pilot whales and
common dolphins in the Atlantic
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portion of the Atlantic Ocean,
Caribbean, Gulf of Mexico, Large
Pelagics Longline Fishery, then, and
currently, listed as a Category I fishery.
At the time of the settlement agreement,
the western North Atlantic stocks of
these three species were identified as
strategic stocks.
Based on updated information, the
2005 U.S. Atlantic and Gulf of Mexico
Marine Mammal Stock Assessments
report (SAR) reclassified long- and
short-finned pilot whales as nonstrategic. The SAR indicated that
serious injuries and mortalities in the
Atlantic pelagic longline fishery were
primarily limited to the Mid-Atlantic
Bight (MAB) (Waring et al., 2006).
Although the 2006 SAR lists the status
of long- and short-finned pilot whales as
unknown, the draft 2007 SAR again
reports that the estimated average
annual human-related mortality and
serious injury for the last five years does
not exceed PBR and the stocks are not
strategic (Waring et al., 2007a; Waring et
al., 2007b).
The 2005 SAR also reported that
within the previous five years, there
were no observed serious injuries or
mortalities of common dolphins in the
pelagic longline fishery; therefore, this
stock was reclassified as non-strategic in
the 2005 SAR, based on estimates of
serious injuries and mortalities in both
the pelagic longline fishery as well as
other observed fisheries.
Risso’s dolphins, although not
included in the settlement agreement,
also sustain serious injuries and
mortalities incidental to the Atlantic
pelagic longline fishery.
For Risso’s dolphins and long-finned
and short-finned pilot whales, estimated
serious injury and mortality levels in
the pelagic longline fishery exceed the
insignificance threshold but do not
exceed the PBR level for the stocks.
Because these species are below PBR
and considered non-strategic stocks but
interact with a Category I fishery, NMFS
directed the PLTRT to develop and
submit a draft Take Reduction Plan to
the agency within 11 months, in
accordance with the long-term goal of
MMPA section 118, focusing on
reducing incidental mortalities and
serious injuries of pilot whales and
Risso’s dolphins to a level approaching
a zero mortality and serious injury rate
within five years of implementation of
the plan.
History of the PLTRT
In accordance with the MMPA and
the settlement agreement, NMFS
convened the PLTRT in June 2005.
NMFS announced the establishment of
the PLTRT on June 22, 2005, in the
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Federal Register (70 FR 36120). NMFS
selected team members according to
guidance provided in MMPA section
118(f)(6)(C). NMFS strove to select an
experienced and committed team with a
balanced representation of stakeholders.
Members of the PLTRT included
fishermen and representatives of the
Atlantic pelagic longline fishing
industry, environmental groups, marine
mammal biologists, fisheries biologists,
and representatives of the Mid-Atlantic
Fishery Management Council, the
Marine Mammal Commission, and
NMFS.
Four professionally facilitated
meetings and two full-team conference
calls were held between June 2005 and
May 2006. During these meetings,
NMFS presented abundance estimates,
serious injury and mortality estimates of
pilot whales and Risso’s dolphins,
characterization and regulatory
structure of the pelagic longline fishery,
and analyses of observer, logbook, and
other fisheries data to the PLTRT. In
addition, NMFS developed a predictive
model that analyzed a number of
variables (e.g., environmental factors,
gear types, etc.) to determine which
variables may be useful in predicting
and/or minimizing interactions between
marine mammals and longline gear as
well as possible impacts on target
species catch and bycatch of other
protected species (e.g., sea turtles). Each
meeting included facilitated discussions
to draft and revise various components
of the PLTRP, with an emphasis on
management and research
recommendations. The PLTRT reached
consensus at the May 2006 meeting, and
on June 8, 2006, submitted to NMFS a
Draft PLTRP including
recommendations for bycatch reduction
measures, as well as research needs and
other non-regulatory measures (PLTRT,
2006).
Distribution, Stock Structure, and
Abundance of Pilot Whales
In the MAB, the Atlantic pelagic
longline fishery interacts with two
species of pilot whales that occur in that
area. Long-finned pilot whales are
distributed worldwide in cold temperate
waters in both the Northern (North
Atlantic) and Southern Hemispheres. In
the North Atlantic, the species is
broadly distributed and thought to occur
from 40° to 75° N. lat. in the eastern
North Atlantic and from 35° to 65° N.
lat. in the western North Atlantic
(Abend and Smith, 1999). Short-finned
pilot whales are also distributed
worldwide in warm temperate and
tropical waters. In U.S. Atlantic waters,
this species is found in the Gulf of
Mexico (GOM) and in the western North
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Atlantic as far north as the central MAB.
Both species tend to favor the
continental shelf break and slope, as
well as other areas of high relief, but are
also present offshore in the pelagic
environment. In the western North
Atlantic, they may be associated with
the north wall of the Gulf Stream and
with thermal fronts (Waring et al.,
1992).
The two species are difficult to
distinguish during visual abundance
surveys, and therefore, in many cases,
reference is made to the combined
species, Globicephala spp. Due to this
difficulty in species identification, the
species’ boundaries for short-finned and
long-finned pilot whales in the western
North Atlantic have not been clearly
defined. However, their distributions
are thought to overlap along the U.S.
mid-Atlantic coast between 35° and 39°
N. lat. (Payne and Heinemann, 1993;
Bernard and Reilly, 1999). The greatest
area of overlap in distribution of the two
species seems confined to an area along
the shelf edge between 38° and 40° N.
lat. in the MAB, where long-finned pilot
whales are present in winter and
summer and short-finned pilot whales
are present at least in summer (Waring
et al., 2007a).
Stock structure is not well known for
long-finned or short-finned pilot whales
in the North Atlantic. Indirect and
direct studies on long-finned pilot
whales indicate that there is some
degree of stock differentiation within
the North Atlantic (Mercer, 1975; Bloch
and Lastein, 1993; Abend and Smith,
1995; Abend and Smith, 1999; Fullard
et al., 2000). For short-finned pilot
whales, there is no available
information on whether the North
Atlantic stock is subdivided into smaller
stocks.
The total number of pilot whales off
the eastern U.S. and Canadian Atlantic
coast is unknown, although estimates
from particular regions of their habitat
(e.g., continental slope) exist for select
time periods (see Waring et al., 2006 for
a complete summary). Observers at sea
cannot reliably distinguish long- and
short-finned pilot whales visually. As a
result, sightings of pilot whales are not
identified to species and resulting
survey estimates are considered joint
estimates for both species. The best
available estimate for Globicephala spp.
in the U.S. Exclusive Economic Zone
(EEZ) is the sum of the estimates from
the summer 2004 U.S. Atlantic surveys,
31,139 (Coefficient of Variation, or
CV=0.27), where the estimate from the
northern U.S. Atlantic is 15,728
(CV=0.34), and from the southern U.S.
Atlantic is 15,411 (CV=0.43) (Waring et
al., 2006). This joint estimate is the most
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recent available, and these surveys
include the most complete coverage of
the species’ habitats (although the
PLTRT recognized that this estimate
was limited to the U.S. EEZ). For
Globicephala spp., the minimum
population estimate, which accounts for
uncertainty in the best estimate (Wade
and Angliss, 1997), is 24,866.
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Distribution, Stock Structure, and
Abundance of Risso’s Dolphins
Risso’s dolphins occur worldwide in
warm temperate and tropical waters
roughly between 60° N. and 60° S. lat.,
and records of the species in the
western North Atlantic range from
Greenland south, including the Gulf of
Mexico (Kruse et al., 1999). In the U.S.
Atlantic EEZ, the species is most
commonly seen in the MAB shelf edge
year round and is rarely seen in the Gulf
of Maine (Waring et al., 2004). Risso’s
dolphins are pelagic, preferring waters
along the continental shelf edge and
deeper, as well as areas of submerged
relief such as seamounts and canyons
(Kruse et al., 1999). There is no
information available on population
structure for this species.
Abundance estimates for Risso’s
dolphins off the U.S. or Canadian
Atlantic coast are unknown, although
eight estimates from particular regions
of their habitat exist for select time
periods (Waring et al., 2006). Sightings
of Risso’s dolphins are almost
exclusively in the continental shelf edge
and continental slope areas. The best
available abundance estimate for Risso’s
dolphins in the U.S. EEZ is the sum of
the estimates from the summer 2004
U.S. Atlantic surveys, 20,479 (CV=0.59),
where the estimate from the northern
U.S. Atlantic is 15,053 (CV=0.78), and
from the southern U.S. Atlantic is 5,426
(CV=0.540) (Waring et al., 2006). This
joint estimate is the most recent
available, and the surveys have the most
complete coverage of the species’
habitat (although the PLTRT recognized
that this estimate was limited to the U.S.
EEZ). The minimum population
estimate for the western North Atlantic
Risso’s dolphin, which accounts for
uncertainty in the best estimate (Wade
and Angliss, 1997), is 12,920.
Potential Biological Removal and
Serious Injury and Mortality Estimates
PBR is defined as the product of
minimum population size (in this case,
of the portion of the stock surveyed
within the U.S. EEZ), one-half the
maximum productivity rate, and a
recovery factor (MMPA Sec. 3(20), 16
U.S.C. 1362). The maximum
productivity rate for both pilot whales
and Risso’s dolphin is 0.04, the default
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value for cetaceans (Barlow et al., 1995).
The recovery factor, which provides
greater protection for endangered,
depleted, or threatened stocks, or stocks
of unknown status relative to optimum
sustainable population (OSP), is 0.48 for
both species because the CV of the
average mortality estimate is between
0.3 and 0.6 (Wade and Angliss, 1997),
and because both stocks are of unknown
status. The PBR for both species of
western North Atlantic pilot whales
combined (i.e., Globicephala spp.) is
249, and the PBR for the western North
Atlantic stock of Risso’s dolphin is 129
(Waring et al., 2007b).
The 2007 draft SAR reported an
average combined annual serious injury
and mortality incidental to pelagic
longline fishing of 86 pilot whales
(CV=0.16) and 34 Risso’s dolphins
(CV=0.32), based on the years 2001–
2005 (Waring et al., 2007b). However,
more recent estimates (Fairfield-Walsh
and Garrison, 2007; Garrison, 2007)
bring the 5–year average combined
serious injury and mortality for pilot
whales to 109 animals (CV=0.194, years
2002–2006) and for Risso’s dolphins to
20 animals (CV=0.381, years 2002–
2006). Based on this information,
serious injury and mortality of pilot
whales and Risso’s dolphins in the
Atlantic pelagic longline fishery is
below PBR, but exceed the
insignificance threshold. NMFS believes
there is a high level of serious injury
and mortality in the Atlantic pelagic
longline fishery across a number of
marine mammal stocks, warranting the
development and implementation of a
take reduction plan for both pilot whale
and Risso’s dolphin stocks.
Components of the Proposed PLTRP
The proposed PLTRP takes a
stepwise, adaptive management
approach to achieve the long-term goal
of reducing serious injuries and
mortality of pilot whales and Risso’s
dolphins in the Atlantic pelagic longline
fishery to insignificant levels
approaching a zero mortality and
serious injury rate within five years of
implementation. A series of
management measures are designed to
make an initial significant contribution
to reducing serious injury and mortality.
The proposed PLTRP also includes
research recommendations for better
understanding how pilot whales and
Risso’s dolphins interact with longline
gear, as well as assessing current and
potential new management measures.
The PLTRT agreed to evaluate the
success of the final PLTRP at periodic
intervals over the next five years and to
consider amending the PLTRP based on
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the results of ongoing monitoring,
research, and evaluation.
The proposed PLTRP reflects the
results of a predictive model, which
analyzed a number of variables (e.g.,
environmental factors, gear
characteristics, etc.) to determine which
variables may be useful in predicting
and/or minimizing interactions between
marine mammals and longline gear, and
possible impacts on target species catch
and bycatch of other protected species
(e.g., sea turtles). A total of 39 variables
were developed and considered as
potential explanatory factors in the
predictive model. These variables are
classified into five major categories:
environment, space and time, gear type,
effort, and catch. These analyses
employed Pelagic Observer Program
(POP) data collected from 1992 to 2004
and modeled the effects of gear and
environmental factors on the probability
of interacting with pilot whales or
Risso’s dolphins.
The predictive model proved to be an
invaluable tool for the PLTRT to
develop management strategies, since
multiple variables could be tested and
evaluated. For pilot whales, variables
found to have significant correlations
included fishing area (81 percent of
interactions occur along the MAB),
distance from the 200 m (109 fathoms)
isobath (all interactions were observed
within 40 km (21.6 nautical miles, nm)
of the 200 m (109 fathoms) isobath),
water temperature (peak interactions
occur between 70–80° F (21–27° C)),
mainline length (interactions were twice
as high in sets with mainline lengths
greater than 20 nm (37.02 km)) and
swordfish damage (interaction rates
were three times higher in sets with
damage to swordfish catch). Further
analysis of the mainline length effect
indicated that fishing with mainlines
less than 20 nm (37.02 km) in length
resulted in an approximately 50 percent
reduction in the probability of
interacting with a pilot whale relative to
longer mainline lengths. For Risso’s
dolphins, similar results were found,
although correlations were not as strong.
Interactions with Risso’s dolphins were
also significantly correlated with the
Northeast Coastal area and with sets that
used squid as bait.
After considering the results of the
predictive model, the PLTRT
recommended a suite of management
strategies to reduce mortality and
serious injury of pilot whales and
Risso’s dolphins in the Atlantic pelagic
longline fishery. This proposed rule
addresses both the regulatory and nonregulatory measures recommended by
the PLTRT. NMFS proposes to
incorporate nearly all of the PLTRT’s
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consensus recommendations in the
Draft PLTRP into the proposed PLTRP,
with only minor modifications. Changes
from the PLTRT’s consensus
recommendations are noted, along with
the rationale for any proposed change.
One consensus recommendation will
not be implemented through this
proposed rule, but will be implemented
under different authority. Specifically,
the PLTRT recommended NMFS
develop and implement a mandatory
certification program to educate owners
and operators of pelagic longline vessels
about ways to reduce serious injury and
mortality of marine mammal bycatch.
On August 19, 2005, NMFS published a
proposed rule to consolidate the
management of all Atlantic Highly
Migratory Species (HMS) under one
Fishery Management Plan (FMP) (70 FR
48804). The proposed rule included a
certification program to educate vessel
owners and operators on using required
equipment to handle and release sea
turtles and other protected species (with
recertification every three years). The
PLTRT recommended that the
certification program proposed in the
August 2005 Draft Consolidated HMS
FMP and associated proposed rule (70
FR 48804) be expanded to incorporate
information regarding marine mammal
interactions, including:
• Safe handling and release
techniques for marine mammals;
• Current regulations and guidelines
that apply to the fishery, especially
those related to marine mammal
bycatch, and an explanation of the
purpose and justification of those
regulations and guidelines;
• Information from logbooks and
auxiliary forms associated with
particular research projects;
• Guidelines for captain’s
communications;
• Updates on NMFS’ observer
program, including relevant recent
findings;
• Description of research and
monitoring projects aimed at reducing
marine mammal bycatch, including an
explanation of the purpose of this
research and a description of key
research results to date; and
• Information on marine mammal
species identification.
NMFS is proposing to implement the
PLTRT’s recommendation using NMFS’
existing regulatory authority at 50 CFR
635.8, Workshops. On October 2, 2006,
NMFS published the Consolidated HMS
FMP and the associated final rule (71 FR
58058), which requires all HMS longline
fishermen to attend a NMFS workshop
and earn certification in mitigation,
handling, and release techniques for sea
turtles, sea birds, and other protected
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species. This rule provides NMFS with
the authority necessary to implement
the PLTRT’s recommendation without
additional regulation. Since 2007,
NFMS has incorporated education on
careful handling and release techniques
for marine mammals, current
regulations and guidelines that apply to
the fishery related to marine mammal
bycatch, and an explanation of the
purpose and justification of those
regulations and guidelines into these
workshops. NMFS proposes to expand
the content of the workshops as
appropriate to meet the needs of the
PLTRP.
The PLTRT also discussed other
mitigation and conservation measures
that they did not include in their
consensus recommendations because
they were either economically or
technologically infeasible or did not
meet the goals of the MMPA.
Information on these can be reviewed in
the Draft PLTRP (PLTRT, 2006).
Proposed Regulatory Measures
NMFS proposes the following three
regulatory measures: (1) Establish a
Cape Hatteras Special Research Area
(CHSRA), with specific observer and
research participation requirements for
fishermen operating in that area; (2) set
a 20–nm (37.02–km) upper limit on
mainline length for all pelagic longline
sets within the MAB; and (3) develop
and publish an informational placard
that must be displayed in the
wheelhouse and the working deck of all
active pelagic longline vessels in the
Atlantic fishery.
Cape Hatteras Special Research Area
The PLTRT recommended NMFS
designate a special research area
offshore of Cape Hatteras (hereafter
referred to as the CHSRA) with specific
observer and research participation
requirements for fishermen operating in
that area. The proposed CHSRA
includes all waters inside and including
the rectangular boundary described by
the following lines: 35° N. lat., 75° W.
long., 36° 25′ N. lat., and 74° 35′ W.
long. In order to use pelagic longline
gear within this area, the PLTRT
recommended NMFS implement
through regulations the following
requirements: (1) The owner and
operator of the vessel must accept,
facilitate, and be capable of taking
scientific observers; (2) the owner and
operator of the vessel must be both
willing and able to participate in
government-sponsored research
targeting marine mammal bycatch
reduction; pilot whale behavior,
biology, ecology; or other related topics;
and (3) the operator of the vessel must
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maintain daily communications with
other local vessel operators regarding
marine mammal interactions with the
goal of identifying and exchanging
information relevant to avoiding
bycatch of marine mammals and other
protected species.
The proposed CHSRA encompasses a
5,927 sq km (2,288 sq mile) region that
over the past five years has exhibited
both high fishing effort and high pilot
whale bycatch rates. NMFS delineated
the area to encompass the vast majority
of the observed interactions and to
exclude the area where inshore longline
vessels target yellowfin tuna and coastal
sharks, since the inshore area had low
observed interaction rates.
Vessels in the proposed CHSRA
would be required to carry observers
when requested. In the proposed
regulations, vessels deploying or fishing
with pelagic longline gear in the CHSRA
or transiting through the CHSRA with
pelagic longline gear onboard must call
the NMFS Southeast Fisheries Science
Center (SEFSC) at least 48 hours prior
to embarking on the trip. This
requirement would be in addition to any
existing selection and notification
requirement for observer coverage by
the POP. If a vessel is assigned an
observer, the vessel must take the
observer during that trip; if the vessel
refuses to take the observer, the vessel
is prohibited from deploying or fishing
with pelagic longline gear in the CHSRA
or transiting through the CHSRA with
pelagic longline gear onboard. NMFS
also proposes that no waivers be granted
to vessels fishing in the CHSRA that do
not meet observer safety requirements.
The collection of observer data
representing all vessels in an area is
critical not only for obtaining accurate
(i.e., unbiased) estimates of bycatch, but
also for collecting information about
factors that may be important for
mitigating bycatch (NMFS 2004). For
this reason, NMFS believes full
compliance with observer requirements
in the CHSRA is essential. As noted
earlier, vessels that fish primarily in the
MAB have higher observed marine
mammal take rates than those in other
areas. However, 58 percent of pelagic
longline vessels reporting effort in the
MAB between 2001 and 2005 have
never been observed in the MAB. This
is because certain vessels are routinely
exempted from observer coverage
because they do not meet the observer
safety or accommodations requirements,
which may bias observer data (i.e., data
would not be representative of actual
fishing effort). In order forNMFSto
accurately monitor levels of serious
injury and mortality of marine mammals
incidental to the pelagic longline
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fishery, and thereby, monitor the
effectiveness of the final PLTRP, data
collected by observers must be
representative of both fishing effort and
bycatch. By not allowing exemptions for
observer coverage within the CHSRA,
NMFS will be able to improve observer
data and bycatch estimates within the
CHSRA.
In addition to the proposed
requirement for carrying observers,
NMFS proposes requirements for
vessels in the CHSRA to participate in
research. The establishment of the
CHSRA and the research participation
requirement form an essential
component of the proposed PLTRP,
enabling focused research on pilot
whale interactions with the pelagic
longline fishery, thus contributing to
achieving the objectives of the PLTRP.
Obtaining better data for characterizing
fishery interactions is a high priority.
The PLTRT was limited in its ability to
develop management strategies to
reduce the frequency of interactions
between pilot whales and longline
fishing gear due to a lack of information
regarding the nature, timing, and causes
of these interactions. The proposed
CHSRA would enableNMFSto assess
current and potential new management
measures and would be fundamental in
formulating effective bycatch reduction
strategies.
To implement the research
participation requirement, NMFS
proposes that in addition to observing
normal fishing activities, observers also
conduct additional scientific
investigations aboard pelagic longline
vessels in the CHSRA, as authorized by
MMPA section 118(d)(2)(C). These
investigations would be designed to
support the goals of the PLTRP. The
observers will inform vessel operators of
the specific additional investigations
that may be conducted during the trip.
An observer may direct vessel operators
to modify their fishing behavior, gear, or
both. Instead of or in addition to
carrying an observer, vessels may be
required to carry and deploy gear
provided by NMFS or an observer or
modify their fishing practices. By
calling the NMFS SEFSC, per the
observer requirement described above,
vessels would be agreeing to take an
observer and acknowledging they are
both willing and able to participate in
research in the CHSRA without any
compensation. If vessels are assigned
any special research requirements, they
must participate in the research for the
duration of the assignment. If they do
not participate in the research, they are
prohibited from deploying or fishing
with pelagic longline gear in the CHSRA
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or transiting through the CHSRA with
pelagic longline gear onboard.
Although NMFS strongly supports the
PLTRT’s goal of identifying and
exchanging information among vessel
operators relevant to avoiding bycatch
of marine mammals and other protected
species, NMFS is not proposing
regulations to require the operator of the
vessel to maintain daily
communications with other local vessel
operators regarding marine mammal
interactions within the CHSRA.
Implementation of this recommendation
via regulation would require NMFS to
conduct extensive surveillance for
monitoring and enforcement. Even then,
NMFS would rarely have information
on an individual vessel’s fishing
conditions, catch, and bycatch. Thus,
enforcement of such a regulatory
requirement would be impractical.
Available information from three case
studies of voluntary captains’
communication programs supports the
inference that voluntary communication
programs have substantially reduced
fisheries bycatch and provided large
economic benefits that outweigh the
relatively nominal operating costs
(Martin et al., 2005). For this
communication strategy to be effective,
the exchange of information must be
timely, the entire fleet in a region must
cooperate, and it must result in an
action being taken to either avoid or
reduce bycatch (e.g., captains need to
describe the nature of their protected
species interactions, discuss the results
of any mitigation or safe handling/
release measures used, and share best
practices).
Atlantic pelagic longline fishermen
are already motivated to avoid
interactions with marine mammals, as
these interactions can result in
significant economic loss due to loss of
both target catch and gear from
depredation and entanglements,
respectively. Marine mammal
interactions also represent a safety risk
to vessel operators and crew, as pilot
whales caught in gear can be very
dangerous due to their size and strength.
For these reasons, NMFS believes
outreach would be more effective in this
fishery. Therefore, NMFS will work
instead with CHSRA researchers and
fishermen to encourage captains’
communications in the CHSRA through
voluntary cooperation and as part of
ongoing research.
Mainlength Line
NMFS proposes, in accordance with
the PLTRT recommendation, to set a
20–nm (37.02–km) upper limit on
mainline length for all pelagic longline
sets within the MAB, including the
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CHSRA. Operators of individual fishing
vessels would be allowed to fish
multiple sets at one time, if they so
desired, but the mainline length for each
set could not exceed 20 nm (37.02 km).
The predictive model developed for
pilot whales was used to explore the
potential effects of a mandated
reduction in mainline length to less
than or equal to 20 nm (37.02 km). Of
the potential changes to fishing gear
discussed by the PLTRT, this
management measure was the only one
to have a significant effect on pilot
whale interactions. The predictive
model estimates a reduction in pilot
whale interactions of approximately 26
percent when longlines in the MAB are
limited to less than 20 nm (37.02 km)
in length. This reduction assumes that
fishermen will sometimes fish
additional sets to compensate for hooks
lost by limiting mainline length to 20
nm (37.02 km). The PLTRT considered
a 50 percent compensation in fishing
effort for lost hooks a reasonable
scenario.
At NMFS’ discretion, per the PLTRT’s
recommendation, NMFS may waive this
restriction in the CHSRA in specific
cases to support research for reducing
bycatch of marine mammals in the
pelagic longline fishery. In cases where
NMFS intends to waive this restriction,
NMFS will consult with the PLTRT and
publish a notice of the decision in the
Federal Register.
Careful Handling and Release
Guidelines Posting Requirement
The PLTRT recommended NMFS
develop and publish an informational
placard that must be displayed in the
wheelhouse and on the working deck of
all active pelagic longline vessels in the
Atlantic fishery. The placard would be
based on the existing marine mammal
careful handling and release guidelines
for pelagic longline gear. The PLTRT
specified the placard should draw on
information presented in a mandatory
certification program and reference
filling out a Marine Mammal Injury and
Mortality Reporting Form for every
marine mammal interaction as required
by MMPA section 118(e) and 50 CFR
229.6.
NMFS proposes to implement this
PLTRT recommendation. NMFS
believes this proposed action would
facilitate the careful handling and
release of any pilot whale, Risso’s
dolphin, or other small cetacean caught
incidentally during pelagic longline
fishing. The posting requirement would
ensure NMFS’ guidelines are readily
available for reference during a capture
or entanglement event.
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Proposed Non-regulatory Measures
The PLTRT recommended
implementing the following nonregulatory measures: (1) Provide for 12
to 15 percent observer coverage
throughout all Atlantic pelagic longline
fisheries that interact with pilot whales
or Risso’s dolphins; (2) encourage vessel
operators (i.e., captains) throughout the
fishery to maintain daily
communications with other local vessel
captains regarding protected species
interactions, with the goal of identifying
and exchanging information relevant to
avoiding protected species bycatch; (3)
update careful handling/release
guidelines, equipment, and methods;
and (4) provide quarterly reports of
marine mammal interactions in the
pelagic longline fishery to the PLTRT.
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Increased Observer Coverage
The PLTRT recommended NMFS
increase observer coverage to 12 to 15
percent throughout all Atlantic pelagic
longline fisheries that interact with pilot
whales and Risso’s dolphins to ensure
representative sampling of fishing effort.
They specified sampling should be
designed to achieve statistical reliability
of marine mammal bycatch estimates
and should also take into account the
objectives of marine mammal bycatch
reduction. If resources are not available
to provide such observer coverage for all
fisheries, regions, and seasons, the
PLTRT recommended NMFS allocate
observer coverage to fisheries, regions,
and seasons with the highest observed
or reported bycatch rates of pilot
whales. The PLTRT recommended
additional coverage be achieved by
either increasing the number of NMFS
observers who have been specially
trained to collect additional information
supporting marine mammal research, or
by allowing designated and speciallytrained ‘‘marine mammal observers’’
(deployed by either NMFS or
cooperating researchers) who would
supplement the traditional observer
coverage.
NMFS proposes to implement this
recommendation within the constraints
of available funding. A simulation
analysis evaluating the effects of
increased observer coverage on the
precision of bycatch estimates
indicated: (1) 12 to 15 percent observer
coverage would result in the most
significant gains in precision, (2) setting
a higher target in this range would
‘‘guard’’ against unforeseen problems
placing observers on vessels, and (3)
further increases in coverage would
yield relatively little additional
precision despite significantly higher
costs. Pilot whales are primarily
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observed to interact with the longline
fishery in the MAB and Northeast
Coastal areas; Risso’s dolphins interact
with the fishery in these areas as well
as the Northeast Distant area. Based on
these observations, NMFS proposes to,
within the constraints of available
funding, increase observer coverage to
12 to 15 percent, in order of priority, in
the (1) CHSRA, (2) MAB, and (3) other
areas, such as Northeast Coastal. While
this measure is geared towards
improving the precision of serious
injury and mortality estimates,
additional coverage would also better
characterize fishing operations and
marine mammal behavior, facilitate
collection of data needed for research,
and increase opportunities to collect
biopsy samples from hooked or
entangled marine mammals.
Captains’ Communications
The PLTRT recommended NMFS
encourage vessel operators (i.e.,
captains) to maintain daily
communication with other local vessel
operators regarding protected species
interactions throughout the Atlantic
pelagic longline fishery with the goal of
identifying and exchanging information
relevant to avoiding protected species
bycatch. Captains’ communication were
considered as both a strategy for
avoiding marine mammals’ exposure to
vessels and gear and as a strategy for
reducing the probability of an
interaction once marine mammals are in
the vicinity of the gear.
NMFS is proposing to implement this
non-regulatory recommendation. The
basis for NMFS’ support of a voluntary
captains’ communications program is
provided in the discussion of the
CHSRA.
Careful Handling and Release
Guidelines
The PLTRT recommended NMFS
update the guidelines for careful
handling and release of entangled or
hooked marine mammals. They
recommended NMFS’ guidelines
include descriptions of appropriate
equipment and methods. They also
encouraged both NMFS and the pelagic
longline industry to develop new
technologies, equipment, and methods
for safer and more effective handling
and release of entangled or hooked
marine mammals. They recommended
developments be evaluated carefully
and incorporated into revised guidelines
for careful handling and release of
marine mammals when appropriate.
In the winter of 2006, in preparation
for the workshops for HMS fishermen,
NMFS worked with the PLTRT and
other NMFS staff in updating a
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preexisting placard to reflect the best
available information on careful
handling and release of marine
mammals. This version of the placard
has been distributed at the training
workshops in 2007 and 2008. NMFS
proposes to periodically update the
guidelines per the PLTRT’s
recommendation, based on any new
technologies, equipment, and methods
for safer and more effective handling
and release of entangled or hooked
marine mammals.
Additional Research and Data
Collection
The PLTRT also recommended short-,
medium-, and long-duration research
and data collection goals designed to
enhance the success of the PLTRP.
While the predictive model provided
tremendous guidance to the PLTRT,
there is a significant lack of information
concerning how pilot whales and
Risso’s dolphins interact with the
pelagic longline fishery. Thus, many of
the research recommendations are
general in scope and applicable to both
pilot whales and Risso’s dolphins
unless specified otherwise. The
complete list of these recommendations
can be found in Section IX of the Draft
PLTRP (PLTRT, 2006). The PLTRT
recommended that priority be given to:
(1) research on species that are closest
to or exceed PBR levels; (2) research to
evaluate the effects of implemented
management measures, and (3) research
on species specific abundance,
mortality, and post-hooking
survivorship. The PLTRT also
recommended that, as funds become
available for pelagic longline take
reduction-related research, a subgroup
of the PLTRT be convened to advise on
selection of research projects based on
priorities and the amount of funds
available.
NMFS proposes to pursue the
additional research and data collection
goals outlined by the PLTRT, within the
constraints of available funding.
Further, NMFS proposes to consider the
PLTRT’s recommendations for
additional research and data collection
when establishing NMFS’ funding
priorities. NMFS would follow the
recommendations to the extent that
good scientific practice and resources
allow. As feasible and appropriate,
NMFS would consult with PLTRT
members during this process.
Adaptive Management and Monitoring
The proposed PLTRP takes a
stepwise, adaptive management
approach to achieving the long-term
goal of reducing, within five years of its
implementation, serious injuries and
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mortalities of pilot whales and Risso’s
dolphins in the Atlantic pelagic longline
fishery to insignificant levels
approaching a zero mortality and
serious injury rate. A series of
monitoring and evaluation steps are
built into the five-year implementation
phase of the proposed PLTRP.
Under the proposed PLTRP, the
PLTRT will periodically: (1) analyze the
status of scientific information on pilot
whales and Risso’s dolphins, (2)
evaluate the effectiveness of the PLTRP,
and (3) adjust the PLTRP’s management
measures and research program, as
appropriate, to ensure that the goal of
the PLTRP will be met within 5 years
of its implementation. Per the PLTRT’s
request, NMFS will provide any updates
available on the following types of
information to inform these periodic
assessments: (1) Status of PLTRP
implementation, (2) SARs; (3) habitat
analyses; (4) data collection and
research findings; (5) voluntary efforts
carried out by the pelagic longline
industry; (6) status of observer coverage;
and (7) predictive model results for pilot
whales and Risso’s dolphins, based on
updated data.
The timing of these assessments
would be tied to both the availability of
data and the time needed to adequately
evaluate the effectiveness of
management measures or the results of
the research program. As requested by
the PLTRT, NMFS will provide them
with quarterly reports of bycatch of
marine mammals in the pelagic longline
fishery. The quarterly reports will help
determine when it will be timely and
useful for the PLTRT to reconvene. In
conjunction with the receipt of quarterly
bycatch reports, the PLTRT agreed to
assess the merits of convening future
PLTRT meetings, either in-person or by
teleconference.
Public Comments Solicited
NMFS is soliciting comments on any
aspect of this proposed rule, including
the development and implementation of
the PLTRP pursuant to MMPA section
118(f)(1) and the specific regulatory and
non-regulatory measures proposed.
NMFS is particularly interested in
comments concerning (1) NMFS’ view
that the level of bycatch signifies a high
level of bycatch in the Atlantic pelagic
longline fishery across a number of
marine mammal stocks, warranting the
development and implementation of a
take reduction plan for pilot whale and
Risso’s dolphin stocks, (2) NMFS’
decision to implement the PLTRT’s
recommendation for a mandatory
certification program using
NMFS’existing authority at 50 CFR
635.8, Workshops, (3) the research
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recommendations and priorities for
better understanding how pilot whales
and Risso’s dolphins interact with
longline gear, as well as for assessing
current and potential management
measures, (4) the CHSRA requirements,
(5) expected fishing effort compensation
under the proposed mainline length
restriction, and (6) information on
careful handling and release of marine
mammals.
Classification
NMFS determined that this action is
consistent to the maximum extent
practicable with the enforceable policies
of the approved coastal management
programs of North Carolina, Virginia,
Maryland, Delaware, New Jersey, New
York, Connecticut, Rhode Island, and
Massachusetts. This determination has
been submitted for review by the
responsible state agencies under section
307 of the Coastal Zone Management
Act.
This proposed rule does not contain
policies with federalism implications
under Executive Order 13132.
This proposed rule has been
determined to be not significant under
Executive Order 12866.
NMFS prepared an initial regulatory
flexibility analysis (IRFA), pursuant to
section 603 of the Regulatory Flexibility
Act (5 U.S.C. 601 et seq.), that describes
the economic impact this proposed rule,
if adopted, would have on small
entities. A description of the action,
why it is being considered, and its legal
basis are included in the preamble of
this proposed rule. A summary of the
analysis follows. For a copy of this
analysis, see the ADDRESSES section.
NMFS considers all HMS permit
holders to be small entities because they
either had average annual receipts less
than $4.0 million for fish-harvesting,
average annual receipts less than $6.5
million for charter/party boats, 100 or
fewer employees for wholesale dealers,
or 500 or fewer employees for seafood
processors. These are the Small
Business Administration (SBA) size
standards for defining a small versus
large business entity in this industry.
An ‘‘active’’ pelagic longline vessel is
considered to be a vessel that reported
pelagic longline activity in the HMS
logbook. The number of active HMS
pelagic longline vessels has been
precipitously decreasing since 1994. In
the MAB, only 85 unique pelagic
longline vessels reported effort between
2001 and 2006. The number of vessels
fishing in the MAB has declined in
recent years, and between 2003 and
2006, the number of vessels reporting
effort in the MAB ranged between 38
and 41.
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The alternatives considered and
analyzed include four options.
Alternative 1 (the no action alternative)
would maintain the status quo
management for the pelagic longline
fishery under the HMS FMP. Alternative
2 would implement only the nonregulatory components recommended in
the Draft PLTRP, while allowing time
for collecting additional scientific data
prior to implementing regulatory
measures. Alternative 3, the preferred
alternative, would limit the mainline
length to 20 nm or less within the MAB,
designate the CHSRA with associated
observer and research participation
requirements, and require all pelagic
longline vessels to post an informational
placard on careful handling and release
of marine mammals. Alternative 4
would include a six-month closure
(July-December) of the southern MAB
sub-regional area and a year-round
mainline length reduction throughout
the MAB, inclusive of that sub-regional
area.
Under the status quo alternative, it is
estimated that the Atlantic pelagic
longline fleet generates an estimated
$24.6 million in revenues. Applying
average species weights reported to
dealers in 2004 and the average 2006 exvessel prices reported by dealers in the
MAB region, NMFS estimated the
potential change in fishery revenues
from the mainline length restriction,
depending on the level of compensation
in fishing effort, to range from an
increase of $777,747 (full compensation
in the number of hooks fished) to a loss
of $819,523 (no compensation in the
number of hooks fished), with an
estimated loss of $239,383 with 50
percent compensation in the number of
hooks fished. This change in revenues
would impact 41 or fewer vessels per
year based on current trends in the
number of active pelagic longline
vessels and the number of vessels that
operated in the MAB in 2006. If one
assumes that 41 vessels are affected by
this restriction, then the estimated
annual impact per vessel ranges from an
increase of $18,969 per vessel to a
decrease of $19,988 per vessel, with an
estimated decrease of $5,838 under the
most likely scenarios (50 percent
compensation in fishing effort).
The economic costs of Alternative 4
were evaluated based upon historical
observed catch rates and reported effort
in the MAB fishing area only for the
period 2002 to 2004. The impact of the
closure of the southern region of the
MAB from July-December was estimated
by assuming no catch in that area,
resulting in a total estimated cost of
$770,000. The combined effect of the 6–
month closure and the mainline length
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restriction through the MAB resulted in
an estimated cost of $1.64 million,
reflecting only lost catch and assuming
no compensation or redistribution of
effort. The reduction in revenues would
impact 41 or fewer vessels per year
based on the current trends in the
number of active pelagic longline
vessels and the number of vessels that
operated in the MAB in 2006. If one
assumes that 41 vessels would be
affected by this restriction, then per
vessel impacts are estimated to be
$40,000.
Alternative 1 (the no action
alternative) and Alternative 2 were not
selected because they were not expected
to meet the conservation objectives of
the proposed rule or the goals in MMPA
section 118. Both Alternative 3 and
Alternative 4 would meet the objectives
of the proposed rule. Alternative 4 was
not selected because, although it would
meet objectives of the proposed rule, it
would likely result in larger economic
impacts to small entities than the
preferred alternative.
References Cited
A complete list of all references cited
in this proposed rule can be found on
the PLTRT website at https://
www.nmfs.noaa.gov/pr/interactions/trt/
teams.htm#pl-trt.htm and the NMFS
Southeast Regional Office website at
https://sero.nmfs.noaa.gov/pr/pr.htm,
and is available upon request from the
NMFS Southeast Regional Office in St.
Petersburg, FL (see ADDRESSES).
List of Subjects in 50 CFR Part 229
Administrative practice and
procedure, Fisheries, Reporting and
recordkeeping requirements.
Dated: June 18, 2008.
John Oliver,
Deputy Assistant Administrator for
Operations, National Marine Fisheries
Service.
For the reasons set out in the
preamble, 50 CFR part 229 is proposed
to be amended as follows:
PART 229—AUTHORIZATION FOR
COMMERCIAL FISHERIES UNDER THE
MARINE MAMMAL PROTECTION ACT
OF 1972
1. The authority citation for part 229
continues to read as follows:
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Authority: 16 U.S.C. 1361 et seq.
2. In subpart A, § 229.3, paragraphs (t)
and (u) are added to read as follows:
§ 229.3
Prohibitions.
*
*
*
*
*
(t) It is prohibited to deploy or fish
with pelagic longline gear in the MidAtlantic Bight unless the vessel:
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(1) Complies with the placard posting
requirement specified in § 229.36(c);
and
(2) Complies with the gear restrictions
specified in § 229.36(e).
(u) It is prohibited to deploy or fish
with pelagic longline gear in the CHSRA
or to transit through the CHSRA with
pelagic longline gear onboard unless the
vessel is in compliance with the
observer and research requirements
specified in § 229.36(d).
3. In subpart C, § 229.36 is added to
read as follows:
§ 229.36 Atlantic Pelagic Longline Take
Reduction Plan (PLTRP).
(a) Purpose and scope. The purpose of
this section is to implement the PLTRP
to reduce incidental mortality and
serious injury of long-finned and shortfinned pilot whales and Risso’s
dolphins in the Atlantic pelagic longline
fishery off the U.S. east coast, a
component of the Atlantic Ocean,
Caribbean, Gulf of Mexico large pelagics
longline fishery, as delineated on the
MMPA List of Fisheries.
(1) Persons subject to this section. The
regulations in this section apply to the
owner and operator of any vessel that
has been issued or is required to be
issued an Atlantic HMS tunas,
swordfish, or shark permit under § 635.4
or § 635.32 and that has pelagic longline
gear onboard as defined under
§ 635.21(c).
(2) Geographic scope. The geographic
scope of the PLTRP is the Atlantic
federal EEZ off the U.S. East Coast. The
regulations specified in paragraphs (b)
through (e) of this section apply to all
U.S. Atlantic pelagic longline vessels
operating in the EEZ portion of the MidAtlantic Bight.
(b) Definitions. In addition to the
definitions contained in the MMPA and
§§ 216.3 and 229.2 of this chapter, the
following definitions apply.
(1) CHSRA (Cape Hatteras Special
Research Area) means all waters inside
and including the rectangular boundary
described by the following lines: 35° N.
lat., 75° W. long., 36° 25′ N. lat., and 74°
35′ W. long.
(2) Mid-Atlantic Bight means the area
bounded by straight lines connecting
the mid-Atlantic states’ internal waters
and extending to 71° W. long. between
35° N. lat. and 43° N. lat.
(3) Observer means an individual
authorized by NMFS, or a designated
contractor, placed aboard a commercial
fishing vessel, to record information on
marine mammal interactions, fishing
operations, marine mammal life history
information, and other scientific data; to
collect biological specimens; and to
perform other scientific investigations.
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(4) Pelagic longline has the same
meaning as in § 635.2 of this title.
(c) Marine Mammal Handling and
Release Placard. The placard, ‘‘Marine
Mammal Handling/Release Guidelines:
A Quick Reference for Atlantic Pelagic
Longline Gear,’’ must be kept posted
inside the wheelhouse and on the
working deck. You may contact the
NMFS Southeast Regional Office at
(727) 824–5312 to request additional
copies of the placard.
(d) CHSRA—(1) Special observer
requirements. If you deploy or fish with
pelagic longline gear in the CHSRA or
transit through the CHSRA with pelagic
longline gear onboard, or intend to do
so, you must call NMFS Southeast
Fisheries Science Center, 1–800–858–
0624, at least 48 hours prior to
embarking on your trip. This
requirement is in addition to any
existing selection and notification
requirement for observer coverage by
the Pelagic Observer Program. If you are
assigned an observer, you must take the
observer during that trip. If you do not
take the observer, you are prohibited
from deploying or fishing with pelagic
longline gear in the CHSRA or transiting
through the CHSRA with pelagic
longline gear onboard. You must
comply with all provisions of § 229.7,
Monitoring of incidental mortalities and
serious injuries. In addition, all
provisions of § 600.746, Observers,
apply. No waivers will be granted under
§ 229.7(c)(3) or § 600.746(f). A vessel
that would otherwise be required to
carry an observer, but is inadequate or
unsafe for purposes of carrying an
observer and for allowing operation of
normal observer functions, is prohibited
from deploying or fishing with pelagic
longline gear in the CHSRA or transiting
through the CHSRA with pelagic
longline gear onboard.
(2) Special research requirements. In
addition to observing normal fishing
activities, observers may conduct
additional scientific investigations
aboard your vessel designed to support
the goals of the PLTRP. The observer
will inform you of the specific
additional investigations that may be
conducted during your trip. An observer
may direct you to modify your fishing
behavior, gear, or both. Instead of
carrying an observer, you may be
required to carry and deploy gear
provided by NMFS or an observer or
modify your fishing practices. By calling
in per § 229.36(d)(1), you are agreeing to
take an observer. You are also
acknowledging you are both willing and
able to participate in research, as per
this paragraph, in the CHSRA consistent
with the PLTRP without any
compensation. If you are assigned any
E:\FR\FM\24JNP1.SGM
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ebenthall on PRODPC60 with PROPOSALS
special research requirements, you must
participate in the research for the
duration of the assignment. If you do
not participate in the research, you are
prohibited from deploying or fishing
with pelagic longline gear in the CHSRA
or transiting through the CHSRA with
pelagic longline gear onboard.
VerDate Aug<31>2005
15:03 Jun 23, 2008
Jkt 214001
(e) Gear restrictions. No person may
deploy a pelagic longline that exceeds
20 nautical miles (nm) (37.04 km) in
length in the Mid-Atlantic Bight,
including in the CHSRA, unless they
have a written letter of authorization
from the Director, NMFS Southeast
Fishery Science Center to use a pelagic
PO 00000
Frm 00039
Fmt 4702
Sfmt 4702
35631
longline exceeding 20 nm in the CHSRA
in support research for reducing bycatch
of marine mammals in the pelagic
longline fishery.
[FR Doc. E8–14274 Filed 6–23–08; 8:45 am]
BILLING CODE 3510–22–S
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Agencies
[Federal Register Volume 73, Number 122 (Tuesday, June 24, 2008)]
[Proposed Rules]
[Pages 35623-35631]
From the Federal Register Online via the Government Printing Office [www.gpo.gov]
[FR Doc No: E8-14274]
=======================================================================
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DEPARTMENT OF COMMERCE
National Oceanic and Atmospheric Administration
50 CFR Part 229
[Docket No. 070717352-8511-0]
RIN 0648-AV65
Taking of Marine Mammals Incidental to Commercial Fishing
Operations; Atlantic Pelagic Longline Take Reduction Plan
AGENCY: National Marine Fisheries Service (NMFS), National Oceanic and
Atmospheric Administration (NOAA), Commerce.
ACTION: Proposed rule; notice of availability of draft take reduction
plan; request for comments.
-----------------------------------------------------------------------
SUMMARY: The National Marine Fisheries Service (NMFS) announces the
initial determination that the pelagic longline fishery has a high
level of mortality and serious injury across a number of marine mammal
stocks, and proposes regulations to implement the Atlantic Pelagic
Longline Take Reduction Plan (PLTRP) to reduce serious injuries and
mortalities of pilot whales and Risso's dolphins in the Atlantic
pelagic longline fishery. The PLTRP is based on consensus
recommendations submitted by the Atlantic Pelagic Longline Take
Reduction Team (PLTRT). This action is necessary because current
serious injury and mortality rates of pilot whales and Risso's dolphins
incidental to the Atlantic pelagic longline component of a Category I
fishery are above insignificant levels approaching a zero mortality and
serious injury rate (zero mortality rate goal, or ZMRG), and therefore,
inconsistent with the long-term goal of the Marine Mammal Protection
Act (MMPA). The PLTRP is intended to meet the statutory mandates and
requirements of the MMPA through both regulatory and non-regulatory
measures, including a special research area, gear modifications,
outreach material, observer coverage, and captains' communications.
DATES: Written comments on the proposed rule must be received no later
than 5 p.m. eastern time on September 22, 2008.
ADDRESSES: You may submit comments, identified by the Regulatory
Information Number (RIN) 0648-AV65, by any of the following methods:
Electronic Submissions: Submit all electronic public
comments via the Federal eRulemaking Portal https://www.regulations.gov.
Facsimile (fax): 727 824-5309, Attn: Assistant Regional
Administrator, Protected Resources.
Mail: Assistant Regional Administrator for Protected
Resources, NMFS, 263 13th Avenue South, St. Petersburg, FL 33701.
Instructions: All comments received are a part of the public record
and will generally be posted to https://www.regulations.gov without
change. All Personal Identifying Information (for example, name,
address, etc.) voluntarily submitted by the commenter may be publicly
accessible. Do not submit Confidential Business Information or
otherwise sensitive or protected information.
NMFS will accept anonymous comments. Attachments to electronic
comments will be accepted in Microsoft Word, Excel, WordPerfect, or
Adobe PDF file formats only.
This proposed rule, references, and background documents for the
PLTRP can be downloaded from the Take Reduction web site at https://
www.nmfs.noaa.gov/pr/interactions/trt/teams.htm#pl-trt.htm and the NMFS
Southeast Regional Office website at https://sero.nmfs.noaa.gov/pr/
pr.htm.
FOR FURTHER INFORMATION CONTACT: Laura Engleby or Jennifer Lee, NMFS,
Southeast Region, 727-824-5312, or Kristy Long, NMFS, Office of
Protected Resources, 301-713-2322. Individuals who use
telecommunications devices for the deaf (TDD) may call the Federal
Information Relay Service at 1-800-877-8339 between 8 a.m. and 4 p.m.
eastern time, Monday through Friday, excluding Federal holidays.
SUPPLEMENTARY INFORMATION:
Bycatch Reduction Requirements in the MMPA
Section 118(f)(1) of the MMPA requires NMFS to develop and
implement take reduction plans to assist in the recovery or prevent the
depletion of each strategic marine mammal stock that interacts with
Category I and II fisheries. It also provides NMFS discretion to
develop and implement a take reduction plan for any other marine mammal
stocks that interact with a Category I fishery, which the agency
determines, after notice and opportunity for public comment, has a high
level of mortality and serious injury across a number of such marine
mammal stocks.
The MMPA defines a strategic stock as a marine mammal stock: (1)
for which the level of direct human-caused mortality exceeds the
potential biological removal (PBR) level; (2) which is declining and is
likely to be listed under the Endangered Species Act (ESA) in the
foreseeable future; or (3) which is listed as threatened or endangered
under the ESA or as a depleted species under the MMPA (16 U.S.C.
1362(2)). PBR is the maximum number of animals, not including natural
mortalities, that can be removed annually from a stock, while allowing
that stock to reach or maintain its optimum sustainable population
level. Category I or II fisheries are fisheries that, respectively,
have frequent or occasional incidental mortality and serious injury of
marine mammals.
The immediate goal of a take reduction plan for a strategic stock
is to reduce, within six months of its implementation, the incidental
serious injury or mortality of marine mammals from commercial fishing
to levels less than PBR. The long-term goal is to reduce, within five
years of its implementation, the incidental serious injury and
mortality of marine mammals from commercial fishing operations to
insignificant levels approaching a zero serious injury and mortality
rate, taking into account the economics of the fishery, the
availability of existing technology, and existing state or regional
fishery management plans. The insignificance threshold, or upper limit
of annual incidental mortality and serious injury of marine mammal
stocks by commercial fisheries that can be considered insignificant
levels approaching a zero mortality and serious injury rate, has been
defined at 50 CFR 229.2 as 10 percent of the PBR for a stock of marine
mammals.
Impetus and Scope of the Plan
The impetus for this plan was a 2003 settlement agreement between
NMFS and the Center for Biological Diversity (CBD), that required the
convening of a Take Reduction Team (the PLTRT) under the MMPA by June
30, 2005, to address serious injury and mortality of short- and long-
finned pilot whales and common dolphins in the Atlantic
[[Page 35624]]
portion of the Atlantic Ocean, Caribbean, Gulf of Mexico, Large
Pelagics Longline Fishery, then, and currently, listed as a Category I
fishery. At the time of the settlement agreement, the western North
Atlantic stocks of these three species were identified as strategic
stocks.
Based on updated information, the 2005 U.S. Atlantic and Gulf of
Mexico Marine Mammal Stock Assessments report (SAR) reclassified long-
and short-finned pilot whales as non-strategic. The SAR indicated that
serious injuries and mortalities in the Atlantic pelagic longline
fishery were primarily limited to the Mid-Atlantic Bight (MAB) (Waring
et al., 2006). Although the 2006 SAR lists the status of long- and
short-finned pilot whales as unknown, the draft 2007 SAR again reports
that the estimated average annual human-related mortality and serious
injury for the last five years does not exceed PBR and the stocks are
not strategic (Waring et al., 2007a; Waring et al., 2007b).
The 2005 SAR also reported that within the previous five years,
there were no observed serious injuries or mortalities of common
dolphins in the pelagic longline fishery; therefore, this stock was
reclassified as non-strategic in the 2005 SAR, based on estimates of
serious injuries and mortalities in both the pelagic longline fishery
as well as other observed fisheries.
Risso's dolphins, although not included in the settlement
agreement, also sustain serious injuries and mortalities incidental to
the Atlantic pelagic longline fishery.
For Risso's dolphins and long-finned and short-finned pilot whales,
estimated serious injury and mortality levels in the pelagic longline
fishery exceed the insignificance threshold but do not exceed the PBR
level for the stocks. Because these species are below PBR and
considered non-strategic stocks but interact with a Category I fishery,
NMFS directed the PLTRT to develop and submit a draft Take Reduction
Plan to the agency within 11 months, in accordance with the long-term
goal of MMPA section 118, focusing on reducing incidental mortalities
and serious injuries of pilot whales and Risso's dolphins to a level
approaching a zero mortality and serious injury rate within five years
of implementation of the plan.
History of the PLTRT
In accordance with the MMPA and the settlement agreement, NMFS
convened the PLTRT in June 2005. NMFS announced the establishment of
the PLTRT on June 22, 2005, in the Federal Register (70 FR 36120). NMFS
selected team members according to guidance provided in MMPA section
118(f)(6)(C). NMFS strove to select an experienced and committed team
with a balanced representation of stakeholders. Members of the PLTRT
included fishermen and representatives of the Atlantic pelagic longline
fishing industry, environmental groups, marine mammal biologists,
fisheries biologists, and representatives of the Mid-Atlantic Fishery
Management Council, the Marine Mammal Commission, and NMFS.
Four professionally facilitated meetings and two full-team
conference calls were held between June 2005 and May 2006. During these
meetings, NMFS presented abundance estimates, serious injury and
mortality estimates of pilot whales and Risso's dolphins,
characterization and regulatory structure of the pelagic longline
fishery, and analyses of observer, logbook, and other fisheries data to
the PLTRT. In addition, NMFS developed a predictive model that analyzed
a number of variables (e.g., environmental factors, gear types, etc.)
to determine which variables may be useful in predicting and/or
minimizing interactions between marine mammals and longline gear as
well as possible impacts on target species catch and bycatch of other
protected species (e.g., sea turtles). Each meeting included
facilitated discussions to draft and revise various components of the
PLTRP, with an emphasis on management and research recommendations. The
PLTRT reached consensus at the May 2006 meeting, and on June 8, 2006,
submitted to NMFS a Draft PLTRP including recommendations for bycatch
reduction measures, as well as research needs and other non-regulatory
measures (PLTRT, 2006).
Distribution, Stock Structure, and Abundance of Pilot Whales
In the MAB, the Atlantic pelagic longline fishery interacts with
two species of pilot whales that occur in that area. Long-finned pilot
whales are distributed worldwide in cold temperate waters in both the
Northern (North Atlantic) and Southern Hemispheres. In the North
Atlantic, the species is broadly distributed and thought to occur from
40[deg] to 75[deg] N. lat. in the eastern North Atlantic and from
35[deg] to 65[deg] N. lat. in the western North Atlantic (Abend and
Smith, 1999). Short-finned pilot whales are also distributed worldwide
in warm temperate and tropical waters. In U.S. Atlantic waters, this
species is found in the Gulf of Mexico (GOM) and in the western North
Atlantic as far north as the central MAB. Both species tend to favor
the continental shelf break and slope, as well as other areas of high
relief, but are also present offshore in the pelagic environment. In
the western North Atlantic, they may be associated with the north wall
of the Gulf Stream and with thermal fronts (Waring et al., 1992).
The two species are difficult to distinguish during visual
abundance surveys, and therefore, in many cases, reference is made to
the combined species, Globicephala spp. Due to this difficulty in
species identification, the species' boundaries for short-finned and
long-finned pilot whales in the western North Atlantic have not been
clearly defined. However, their distributions are thought to overlap
along the U.S. mid-Atlantic coast between 35[deg] and 39[deg] N. lat.
(Payne and Heinemann, 1993; Bernard and Reilly, 1999). The greatest
area of overlap in distribution of the two species seems confined to an
area along the shelf edge between 38[deg] and 40[deg] N. lat. in the
MAB, where long-finned pilot whales are present in winter and summer
and short-finned pilot whales are present at least in summer (Waring et
al., 2007a).
Stock structure is not well known for long-finned or short-finned
pilot whales in the North Atlantic. Indirect and direct studies on
long-finned pilot whales indicate that there is some degree of stock
differentiation within the North Atlantic (Mercer, 1975; Bloch and
Lastein, 1993; Abend and Smith, 1995; Abend and Smith, 1999; Fullard et
al., 2000). For short-finned pilot whales, there is no available
information on whether the North Atlantic stock is subdivided into
smaller stocks.
The total number of pilot whales off the eastern U.S. and Canadian
Atlantic coast is unknown, although estimates from particular regions
of their habitat (e.g., continental slope) exist for select time
periods (see Waring et al., 2006 for a complete summary). Observers at
sea cannot reliably distinguish long- and short-finned pilot whales
visually. As a result, sightings of pilot whales are not identified to
species and resulting survey estimates are considered joint estimates
for both species. The best available estimate for Globicephala spp. in
the U.S. Exclusive Economic Zone (EEZ) is the sum of the estimates from
the summer 2004 U.S. Atlantic surveys, 31,139 (Coefficient of
Variation, or CV=0.27), where the estimate from the northern U.S.
Atlantic is 15,728 (CV=0.34), and from the southern U.S. Atlantic is
15,411 (CV=0.43) (Waring et al., 2006). This joint estimate is the most
[[Page 35625]]
recent available, and these surveys include the most complete coverage
of the species' habitats (although the PLTRT recognized that this
estimate was limited to the U.S. EEZ). For Globicephala spp., the
minimum population estimate, which accounts for uncertainty in the best
estimate (Wade and Angliss, 1997), is 24,866.
Distribution, Stock Structure, and Abundance of Risso's Dolphins
Risso's dolphins occur worldwide in warm temperate and tropical
waters roughly between 60[deg] N. and 60[deg] S. lat., and records of
the species in the western North Atlantic range from Greenland south,
including the Gulf of Mexico (Kruse et al., 1999). In the U.S. Atlantic
EEZ, the species is most commonly seen in the MAB shelf edge year round
and is rarely seen in the Gulf of Maine (Waring et al., 2004). Risso's
dolphins are pelagic, preferring waters along the continental shelf
edge and deeper, as well as areas of submerged relief such as seamounts
and canyons (Kruse et al., 1999). There is no information available on
population structure for this species.
Abundance estimates for Risso's dolphins off the U.S. or Canadian
Atlantic coast are unknown, although eight estimates from particular
regions of their habitat exist for select time periods (Waring et al.,
2006). Sightings of Risso's dolphins are almost exclusively in the
continental shelf edge and continental slope areas. The best available
abundance estimate for Risso's dolphins in the U.S. EEZ is the sum of
the estimates from the summer 2004 U.S. Atlantic surveys, 20,479
(CV=0.59), where the estimate from the northern U.S. Atlantic is 15,053
(CV=0.78), and from the southern U.S. Atlantic is 5,426 (CV=0.540)
(Waring et al., 2006). This joint estimate is the most recent
available, and the surveys have the most complete coverage of the
species' habitat (although the PLTRT recognized that this estimate was
limited to the U.S. EEZ). The minimum population estimate for the
western North Atlantic Risso's dolphin, which accounts for uncertainty
in the best estimate (Wade and Angliss, 1997), is 12,920.
Potential Biological Removal and Serious Injury and Mortality Estimates
PBR is defined as the product of minimum population size (in this
case, of the portion of the stock surveyed within the U.S. EEZ), one-
half the maximum productivity rate, and a recovery factor (MMPA Sec.
3(20), 16 U.S.C. 1362). The maximum productivity rate for both pilot
whales and Risso's dolphin is 0.04, the default value for cetaceans
(Barlow et al., 1995). The recovery factor, which provides greater
protection for endangered, depleted, or threatened stocks, or stocks of
unknown status relative to optimum sustainable population (OSP), is
0.48 for both species because the CV of the average mortality estimate
is between 0.3 and 0.6 (Wade and Angliss, 1997), and because both
stocks are of unknown status. The PBR for both species of western North
Atlantic pilot whales combined (i.e., Globicephala spp.) is 249, and
the PBR for the western North Atlantic stock of Risso's dolphin is 129
(Waring et al., 2007b).
The 2007 draft SAR reported an average combined annual serious
injury and mortality incidental to pelagic longline fishing of 86 pilot
whales (CV=0.16) and 34 Risso's dolphins (CV=0.32), based on the years
2001-2005 (Waring et al., 2007b). However, more recent estimates
(Fairfield-Walsh and Garrison, 2007; Garrison, 2007) bring the 5-year
average combined serious injury and mortality for pilot whales to 109
animals (CV=0.194, years 2002-2006) and for Risso's dolphins to 20
animals (CV=0.381, years 2002-2006). Based on this information, serious
injury and mortality of pilot whales and Risso's dolphins in the
Atlantic pelagic longline fishery is below PBR, but exceed the
insignificance threshold. NMFS believes there is a high level of
serious injury and mortality in the Atlantic pelagic longline fishery
across a number of marine mammal stocks, warranting the development and
implementation of a take reduction plan for both pilot whale and
Risso's dolphin stocks.
Components of the Proposed PLTRP
The proposed PLTRP takes a stepwise, adaptive management approach
to achieve the long-term goal of reducing serious injuries and
mortality of pilot whales and Risso's dolphins in the Atlantic pelagic
longline fishery to insignificant levels approaching a zero mortality
and serious injury rate within five years of implementation. A series
of management measures are designed to make an initial significant
contribution to reducing serious injury and mortality. The proposed
PLTRP also includes research recommendations for better understanding
how pilot whales and Risso's dolphins interact with longline gear, as
well as assessing current and potential new management measures. The
PLTRT agreed to evaluate the success of the final PLTRP at periodic
intervals over the next five years and to consider amending the PLTRP
based on the results of ongoing monitoring, research, and evaluation.
The proposed PLTRP reflects the results of a predictive model,
which analyzed a number of variables (e.g., environmental factors, gear
characteristics, etc.) to determine which variables may be useful in
predicting and/or minimizing interactions between marine mammals and
longline gear, and possible impacts on target species catch and bycatch
of other protected species (e.g., sea turtles). A total of 39 variables
were developed and considered as potential explanatory factors in the
predictive model. These variables are classified into five major
categories: environment, space and time, gear type, effort, and catch.
These analyses employed Pelagic Observer Program (POP) data collected
from 1992 to 2004 and modeled the effects of gear and environmental
factors on the probability of interacting with pilot whales or Risso's
dolphins.
The predictive model proved to be an invaluable tool for the PLTRT
to develop management strategies, since multiple variables could be
tested and evaluated. For pilot whales, variables found to have
significant correlations included fishing area (81 percent of
interactions occur along the MAB), distance from the 200 m (109
fathoms) isobath (all interactions were observed within 40 km (21.6
nautical miles, nm) of the 200 m (109 fathoms) isobath), water
temperature (peak interactions occur between 70-80[deg] F (21-27[deg]
C)), mainline length (interactions were twice as high in sets with
mainline lengths greater than 20 nm (37.02 km)) and swordfish damage
(interaction rates were three times higher in sets with damage to
swordfish catch). Further analysis of the mainline length effect
indicated that fishing with mainlines less than 20 nm (37.02 km) in
length resulted in an approximately 50 percent reduction in the
probability of interacting with a pilot whale relative to longer
mainline lengths. For Risso's dolphins, similar results were found,
although correlations were not as strong. Interactions with Risso's
dolphins were also significantly correlated with the Northeast Coastal
area and with sets that used squid as bait.
After considering the results of the predictive model, the PLTRT
recommended a suite of management strategies to reduce mortality and
serious injury of pilot whales and Risso's dolphins in the Atlantic
pelagic longline fishery. This proposed rule addresses both the
regulatory and non-regulatory measures recommended by the PLTRT. NMFS
proposes to incorporate nearly all of the PLTRT's
[[Page 35626]]
consensus recommendations in the Draft PLTRP into the proposed PLTRP,
with only minor modifications. Changes from the PLTRT's consensus
recommendations are noted, along with the rationale for any proposed
change.
One consensus recommendation will not be implemented through this
proposed rule, but will be implemented under different authority.
Specifically, the PLTRT recommended NMFS develop and implement a
mandatory certification program to educate owners and operators of
pelagic longline vessels about ways to reduce serious injury and
mortality of marine mammal bycatch. On August 19, 2005, NMFS published
a proposed rule to consolidate the management of all Atlantic Highly
Migratory Species (HMS) under one Fishery Management Plan (FMP) (70 FR
48804). The proposed rule included a certification program to educate
vessel owners and operators on using required equipment to handle and
release sea turtles and other protected species (with recertification
every three years). The PLTRT recommended that the certification
program proposed in the August 2005 Draft Consolidated HMS FMP and
associated proposed rule (70 FR 48804) be expanded to incorporate
information regarding marine mammal interactions, including:
Safe handling and release techniques for marine mammals;
Current regulations and guidelines that apply to the
fishery, especially those related to marine mammal bycatch, and an
explanation of the purpose and justification of those regulations and
guidelines;
Information from logbooks and auxiliary forms associated
with particular research projects;
Guidelines for captain's communications;
Updates on NMFS' observer program, including relevant
recent findings;
Description of research and monitoring projects aimed at
reducing marine mammal bycatch, including an explanation of the purpose
of this research and a description of key research results to date; and
Information on marine mammal species identification.
NMFS is proposing to implement the PLTRT's recommendation using
NMFS' existing regulatory authority at 50 CFR 635.8, Workshops. On
October 2, 2006, NMFS published the Consolidated HMS FMP and the
associated final rule (71 FR 58058), which requires all HMS longline
fishermen to attend a NMFS workshop and earn certification in
mitigation, handling, and release techniques for sea turtles, sea
birds, and other protected species. This rule provides NMFS with the
authority necessary to implement the PLTRT's recommendation without
additional regulation. Since 2007, NFMS has incorporated education on
careful handling and release techniques for marine mammals, current
regulations and guidelines that apply to the fishery related to marine
mammal bycatch, and an explanation of the purpose and justification of
those regulations and guidelines into these workshops. NMFS proposes to
expand the content of the workshops as appropriate to meet the needs of
the PLTRP.
The PLTRT also discussed other mitigation and conservation measures
that they did not include in their consensus recommendations because
they were either economically or technologically infeasible or did not
meet the goals of the MMPA. Information on these can be reviewed in the
Draft PLTRP (PLTRT, 2006).
Proposed Regulatory Measures
NMFS proposes the following three regulatory measures: (1)
Establish a Cape Hatteras Special Research Area (CHSRA), with specific
observer and research participation requirements for fishermen
operating in that area; (2) set a 20-nm (37.02-km) upper limit on
mainline length for all pelagic longline sets within the MAB; and (3)
develop and publish an informational placard that must be displayed in
the wheelhouse and the working deck of all active pelagic longline
vessels in the Atlantic fishery.
Cape Hatteras Special Research Area
The PLTRT recommended NMFS designate a special research area
offshore of Cape Hatteras (hereafter referred to as the CHSRA) with
specific observer and research participation requirements for fishermen
operating in that area. The proposed CHSRA includes all waters inside
and including the rectangular boundary described by the following
lines: 35[deg] N. lat., 75[deg] W. long., 36[deg] 25' N. lat., and
74[deg] 35' W. long. In order to use pelagic longline gear within this
area, the PLTRT recommended NMFS implement through regulations the
following requirements: (1) The owner and operator of the vessel must
accept, facilitate, and be capable of taking scientific observers; (2)
the owner and operator of the vessel must be both willing and able to
participate in government-sponsored research targeting marine mammal
bycatch reduction; pilot whale behavior, biology, ecology; or other
related topics; and (3) the operator of the vessel must maintain daily
communications with other local vessel operators regarding marine
mammal interactions with the goal of identifying and exchanging
information relevant to avoiding bycatch of marine mammals and other
protected species.
The proposed CHSRA encompasses a 5,927 sq km (2,288 sq mile) region
that over the past five years has exhibited both high fishing effort
and high pilot whale bycatch rates. NMFS delineated the area to
encompass the vast majority of the observed interactions and to exclude
the area where inshore longline vessels target yellowfin tuna and
coastal sharks, since the inshore area had low observed interaction
rates.
Vessels in the proposed CHSRA would be required to carry observers
when requested. In the proposed regulations, vessels deploying or
fishing with pelagic longline gear in the CHSRA or transiting through
the CHSRA with pelagic longline gear onboard must call the NMFS
Southeast Fisheries Science Center (SEFSC) at least 48 hours prior to
embarking on the trip. This requirement would be in addition to any
existing selection and notification requirement for observer coverage
by the POP. If a vessel is assigned an observer, the vessel must take
the observer during that trip; if the vessel refuses to take the
observer, the vessel is prohibited from deploying or fishing with
pelagic longline gear in the CHSRA or transiting through the CHSRA with
pelagic longline gear onboard. NMFS also proposes that no waivers be
granted to vessels fishing in the CHSRA that do not meet observer
safety requirements.
The collection of observer data representing all vessels in an area
is critical not only for obtaining accurate (i.e., unbiased) estimates
of bycatch, but also for collecting information about factors that may
be important for mitigating bycatch (NMFS 2004). For this reason, NMFS
believes full compliance with observer requirements in the CHSRA is
essential. As noted earlier, vessels that fish primarily in the MAB
have higher observed marine mammal take rates than those in other
areas. However, 58 percent of pelagic longline vessels reporting effort
in the MAB between 2001 and 2005 have never been observed in the MAB.
This is because certain vessels are routinely exempted from observer
coverage because they do not meet the observer safety or accommodations
requirements, which may bias observer data (i.e., data would not be
representative of actual fishing effort). In order forNMFSto accurately
monitor levels of serious injury and mortality of marine mammals
incidental to the pelagic longline
[[Page 35627]]
fishery, and thereby, monitor the effectiveness of the final PLTRP,
data collected by observers must be representative of both fishing
effort and bycatch. By not allowing exemptions for observer coverage
within the CHSRA, NMFS will be able to improve observer data and
bycatch estimates within the CHSRA.
In addition to the proposed requirement for carrying observers,
NMFS proposes requirements for vessels in the CHSRA to participate in
research. The establishment of the CHSRA and the research participation
requirement form an essential component of the proposed PLTRP, enabling
focused research on pilot whale interactions with the pelagic longline
fishery, thus contributing to achieving the objectives of the PLTRP.
Obtaining better data for characterizing fishery interactions is a high
priority. The PLTRT was limited in its ability to develop management
strategies to reduce the frequency of interactions between pilot whales
and longline fishing gear due to a lack of information regarding the
nature, timing, and causes of these interactions. The proposed CHSRA
would enableNMFSto assess current and potential new management measures
and would be fundamental in formulating effective bycatch reduction
strategies.
To implement the research participation requirement, NMFS proposes
that in addition to observing normal fishing activities, observers also
conduct additional scientific investigations aboard pelagic longline
vessels in the CHSRA, as authorized by MMPA section 118(d)(2)(C). These
investigations would be designed to support the goals of the PLTRP. The
observers will inform vessel operators of the specific additional
investigations that may be conducted during the trip. An observer may
direct vessel operators to modify their fishing behavior, gear, or
both. Instead of or in addition to carrying an observer, vessels may be
required to carry and deploy gear provided by NMFS or an observer or
modify their fishing practices. By calling the NMFS SEFSC, per the
observer requirement described above, vessels would be agreeing to take
an observer and acknowledging they are both willing and able to
participate in research in the CHSRA without any compensation. If
vessels are assigned any special research requirements, they must
participate in the research for the duration of the assignment. If they
do not participate in the research, they are prohibited from deploying
or fishing with pelagic longline gear in the CHSRA or transiting
through the CHSRA with pelagic longline gear onboard.
Although NMFS strongly supports the PLTRT's goal of identifying and
exchanging information among vessel operators relevant to avoiding
bycatch of marine mammals and other protected species, NMFS is not
proposing regulations to require the operator of the vessel to maintain
daily communications with other local vessel operators regarding marine
mammal interactions within the CHSRA. Implementation of this
recommendation via regulation would require NMFS to conduct extensive
surveillance for monitoring and enforcement. Even then, NMFS would
rarely have information on an individual vessel's fishing conditions,
catch, and bycatch. Thus, enforcement of such a regulatory requirement
would be impractical.
Available information from three case studies of voluntary
captains' communication programs supports the inference that voluntary
communication programs have substantially reduced fisheries bycatch and
provided large economic benefits that outweigh the relatively nominal
operating costs (Martin et al., 2005). For this communication strategy
to be effective, the exchange of information must be timely, the entire
fleet in a region must cooperate, and it must result in an action being
taken to either avoid or reduce bycatch (e.g., captains need to
describe the nature of their protected species interactions, discuss
the results of any mitigation or safe handling/release measures used,
and share best practices).
Atlantic pelagic longline fishermen are already motivated to avoid
interactions with marine mammals, as these interactions can result in
significant economic loss due to loss of both target catch and gear
from depredation and entanglements, respectively. Marine mammal
interactions also represent a safety risk to vessel operators and crew,
as pilot whales caught in gear can be very dangerous due to their size
and strength. For these reasons, NMFS believes outreach would be more
effective in this fishery. Therefore, NMFS will work instead with CHSRA
researchers and fishermen to encourage captains' communications in the
CHSRA through voluntary cooperation and as part of ongoing research.
Mainlength Line
NMFS proposes, in accordance with the PLTRT recommendation, to set
a 20-nm (37.02-km) upper limit on mainline length for all pelagic
longline sets within the MAB, including the CHSRA. Operators of
individual fishing vessels would be allowed to fish multiple sets at
one time, if they so desired, but the mainline length for each set
could not exceed 20 nm (37.02 km).
The predictive model developed for pilot whales was used to explore
the potential effects of a mandated reduction in mainline length to
less than or equal to 20 nm (37.02 km). Of the potential changes to
fishing gear discussed by the PLTRT, this management measure was the
only one to have a significant effect on pilot whale interactions. The
predictive model estimates a reduction in pilot whale interactions of
approximately 26 percent when longlines in the MAB are limited to less
than 20 nm (37.02 km) in length. This reduction assumes that fishermen
will sometimes fish additional sets to compensate for hooks lost by
limiting mainline length to 20 nm (37.02 km). The PLTRT considered a 50
percent compensation in fishing effort for lost hooks a reasonable
scenario.
At NMFS' discretion, per the PLTRT's recommendation, NMFS may waive
this restriction in the CHSRA in specific cases to support research for
reducing bycatch of marine mammals in the pelagic longline fishery. In
cases where NMFS intends to waive this restriction, NMFS will consult
with the PLTRT and publish a notice of the decision in the Federal
Register.
Careful Handling and Release Guidelines Posting Requirement
The PLTRT recommended NMFS develop and publish an informational
placard that must be displayed in the wheelhouse and on the working
deck of all active pelagic longline vessels in the Atlantic fishery.
The placard would be based on the existing marine mammal careful
handling and release guidelines for pelagic longline gear. The PLTRT
specified the placard should draw on information presented in a
mandatory certification program and reference filling out a Marine
Mammal Injury and Mortality Reporting Form for every marine mammal
interaction as required by MMPA section 118(e) and 50 CFR 229.6.
NMFS proposes to implement this PLTRT recommendation. NMFS believes
this proposed action would facilitate the careful handling and release
of any pilot whale, Risso's dolphin, or other small cetacean caught
incidentally during pelagic longline fishing. The posting requirement
would ensure NMFS' guidelines are readily available for reference
during a capture or entanglement event.
[[Page 35628]]
Proposed Non-regulatory Measures
The PLTRT recommended implementing the following non-regulatory
measures: (1) Provide for 12 to 15 percent observer coverage throughout
all Atlantic pelagic longline fisheries that interact with pilot whales
or Risso's dolphins; (2) encourage vessel operators (i.e., captains)
throughout the fishery to maintain daily communications with other
local vessel captains regarding protected species interactions, with
the goal of identifying and exchanging information relevant to avoiding
protected species bycatch; (3) update careful handling/release
guidelines, equipment, and methods; and (4) provide quarterly reports
of marine mammal interactions in the pelagic longline fishery to the
PLTRT.
Increased Observer Coverage
The PLTRT recommended NMFS increase observer coverage to 12 to 15
percent throughout all Atlantic pelagic longline fisheries that
interact with pilot whales and Risso's dolphins to ensure
representative sampling of fishing effort. They specified sampling
should be designed to achieve statistical reliability of marine mammal
bycatch estimates and should also take into account the objectives of
marine mammal bycatch reduction. If resources are not available to
provide such observer coverage for all fisheries, regions, and seasons,
the PLTRT recommended NMFS allocate observer coverage to fisheries,
regions, and seasons with the highest observed or reported bycatch
rates of pilot whales. The PLTRT recommended additional coverage be
achieved by either increasing the number of NMFS observers who have
been specially trained to collect additional information supporting
marine mammal research, or by allowing designated and specially-trained
``marine mammal observers'' (deployed by either NMFS or cooperating
researchers) who would supplement the traditional observer coverage.
NMFS proposes to implement this recommendation within the
constraints of available funding. A simulation analysis evaluating the
effects of increased observer coverage on the precision of bycatch
estimates indicated: (1) 12 to 15 percent observer coverage would
result in the most significant gains in precision, (2) setting a higher
target in this range would ``guard'' against unforeseen problems
placing observers on vessels, and (3) further increases in coverage
would yield relatively little additional precision despite
significantly higher costs. Pilot whales are primarily observed to
interact with the longline fishery in the MAB and Northeast Coastal
areas; Risso's dolphins interact with the fishery in these areas as
well as the Northeast Distant area. Based on these observations, NMFS
proposes to, within the constraints of available funding, increase
observer coverage to 12 to 15 percent, in order of priority, in the (1)
CHSRA, (2) MAB, and (3) other areas, such as Northeast Coastal. While
this measure is geared towards improving the precision of serious
injury and mortality estimates, additional coverage would also better
characterize fishing operations and marine mammal behavior, facilitate
collection of data needed for research, and increase opportunities to
collect biopsy samples from hooked or entangled marine mammals.
Captains' Communications
The PLTRT recommended NMFS encourage vessel operators (i.e.,
captains) to maintain daily communication with other local vessel
operators regarding protected species interactions throughout the
Atlantic pelagic longline fishery with the goal of identifying and
exchanging information relevant to avoiding protected species bycatch.
Captains' communication were considered as both a strategy for avoiding
marine mammals' exposure to vessels and gear and as a strategy for
reducing the probability of an interaction once marine mammals are in
the vicinity of the gear.
NMFS is proposing to implement this non-regulatory recommendation.
The basis for NMFS' support of a voluntary captains' communications
program is provided in the discussion of the CHSRA.
Careful Handling and Release Guidelines
The PLTRT recommended NMFS update the guidelines for careful
handling and release of entangled or hooked marine mammals. They
recommended NMFS' guidelines include descriptions of appropriate
equipment and methods. They also encouraged both NMFS and the pelagic
longline industry to develop new technologies, equipment, and methods
for safer and more effective handling and release of entangled or
hooked marine mammals. They recommended developments be evaluated
carefully and incorporated into revised guidelines for careful handling
and release of marine mammals when appropriate.
In the winter of 2006, in preparation for the workshops for HMS
fishermen, NMFS worked with the PLTRT and other NMFS staff in updating
a preexisting placard to reflect the best available information on
careful handling and release of marine mammals. This version of the
placard has been distributed at the training workshops in 2007 and
2008. NMFS proposes to periodically update the guidelines per the
PLTRT's recommendation, based on any new technologies, equipment, and
methods for safer and more effective handling and release of entangled
or hooked marine mammals.
Additional Research and Data Collection
The PLTRT also recommended short-, medium-, and long-duration
research and data collection goals designed to enhance the success of
the PLTRP. While the predictive model provided tremendous guidance to
the PLTRT, there is a significant lack of information concerning how
pilot whales and Risso's dolphins interact with the pelagic longline
fishery. Thus, many of the research recommendations are general in
scope and applicable to both pilot whales and Risso's dolphins unless
specified otherwise. The complete list of these recommendations can be
found in Section IX of the Draft PLTRP (PLTRT, 2006). The PLTRT
recommended that priority be given to: (1) research on species that are
closest to or exceed PBR levels; (2) research to evaluate the effects
of implemented management measures, and (3) research on species
specific abundance, mortality, and post-hooking survivorship. The PLTRT
also recommended that, as funds become available for pelagic longline
take reduction-related research, a subgroup of the PLTRT be convened to
advise on selection of research projects based on priorities and the
amount of funds available.
NMFS proposes to pursue the additional research and data collection
goals outlined by the PLTRT, within the constraints of available
funding. Further, NMFS proposes to consider the PLTRT's recommendations
for additional research and data collection when establishing NMFS'
funding priorities. NMFS would follow the recommendations to the extent
that good scientific practice and resources allow. As feasible and
appropriate, NMFS would consult with PLTRT members during this process.
Adaptive Management and Monitoring
The proposed PLTRP takes a stepwise, adaptive management approach
to achieving the long-term goal of reducing, within five years of its
implementation, serious injuries and
[[Page 35629]]
mortalities of pilot whales and Risso's dolphins in the Atlantic
pelagic longline fishery to insignificant levels approaching a zero
mortality and serious injury rate. A series of monitoring and
evaluation steps are built into the five-year implementation phase of
the proposed PLTRP.
Under the proposed PLTRP, the PLTRT will periodically: (1) analyze
the status of scientific information on pilot whales and Risso's
dolphins, (2) evaluate the effectiveness of the PLTRP, and (3) adjust
the PLTRP's management measures and research program, as appropriate,
to ensure that the goal of the PLTRP will be met within 5 years of its
implementation. Per the PLTRT's request, NMFS will provide any updates
available on the following types of information to inform these
periodic assessments: (1) Status of PLTRP implementation, (2) SARs; (3)
habitat analyses; (4) data collection and research findings; (5)
voluntary efforts carried out by the pelagic longline industry; (6)
status of observer coverage; and (7) predictive model results for pilot
whales and Risso's dolphins, based on updated data.
The timing of these assessments would be tied to both the
availability of data and the time needed to adequately evaluate the
effectiveness of management measures or the results of the research
program. As requested by the PLTRT, NMFS will provide them with
quarterly reports of bycatch of marine mammals in the pelagic longline
fishery. The quarterly reports will help determine when it will be
timely and useful for the PLTRT to reconvene. In conjunction with the
receipt of quarterly bycatch reports, the PLTRT agreed to assess the
merits of convening future PLTRT meetings, either in-person or by
teleconference.
Public Comments Solicited
NMFS is soliciting comments on any aspect of this proposed rule,
including the development and implementation of the PLTRP pursuant to
MMPA section 118(f)(1) and the specific regulatory and non-regulatory
measures proposed. NMFS is particularly interested in comments
concerning (1) NMFS' view that the level of bycatch signifies a high
level of bycatch in the Atlantic pelagic longline fishery across a
number of marine mammal stocks, warranting the development and
implementation of a take reduction plan for pilot whale and Risso's
dolphin stocks, (2) NMFS' decision to implement the PLTRT's
recommendation for a mandatory certification program using
NMFS'existing authority at 50 CFR 635.8, Workshops, (3) the research
recommendations and priorities for better understanding how pilot
whales and Risso's dolphins interact with longline gear, as well as for
assessing current and potential management measures, (4) the CHSRA
requirements, (5) expected fishing effort compensation under the
proposed mainline length restriction, and (6) information on careful
handling and release of marine mammals.
Classification
NMFS determined that this action is consistent to the maximum
extent practicable with the enforceable policies of the approved
coastal management programs of North Carolina, Virginia, Maryland,
Delaware, New Jersey, New York, Connecticut, Rhode Island, and
Massachusetts. This determination has been submitted for review by the
responsible state agencies under section 307 of the Coastal Zone
Management Act.
This proposed rule does not contain policies with federalism
implications under Executive Order 13132.
This proposed rule has been determined to be not significant under
Executive Order 12866.
NMFS prepared an initial regulatory flexibility analysis (IRFA),
pursuant to section 603 of the Regulatory Flexibility Act (5 U.S.C. 601
et seq.), that describes the economic impact this proposed rule, if
adopted, would have on small entities. A description of the action, why
it is being considered, and its legal basis are included in the
preamble of this proposed rule. A summary of the analysis follows. For
a copy of this analysis, see the ADDRESSES section.
NMFS considers all HMS permit holders to be small entities because
they either had average annual receipts less than $4.0 million for
fish-harvesting, average annual receipts less than $6.5 million for
charter/party boats, 100 or fewer employees for wholesale dealers, or
500 or fewer employees for seafood processors. These are the Small
Business Administration (SBA) size standards for defining a small
versus large business entity in this industry. An ``active'' pelagic
longline vessel is considered to be a vessel that reported pelagic
longline activity in the HMS logbook. The number of active HMS pelagic
longline vessels has been precipitously decreasing since 1994. In the
MAB, only 85 unique pelagic longline vessels reported effort between
2001 and 2006. The number of vessels fishing in the MAB has declined in
recent years, and between 2003 and 2006, the number of vessels
reporting effort in the MAB ranged between 38 and 41.
The alternatives considered and analyzed include four options.
Alternative 1 (the no action alternative) would maintain the status quo
management for the pelagic longline fishery under the HMS FMP.
Alternative 2 would implement only the non-regulatory components
recommended in the Draft PLTRP, while allowing time for collecting
additional scientific data prior to implementing regulatory measures.
Alternative 3, the preferred alternative, would limit the mainline
length to 20 nm or less within the MAB, designate the CHSRA with
associated observer and research participation requirements, and
require all pelagic longline vessels to post an informational placard
on careful handling and release of marine mammals. Alternative 4 would
include a six-month closure (July-December) of the southern MAB sub-
regional area and a year-round mainline length reduction throughout the
MAB, inclusive of that sub-regional area.
Under the status quo alternative, it is estimated that the Atlantic
pelagic longline fleet generates an estimated $24.6 million in
revenues. Applying average species weights reported to dealers in 2004
and the average 2006 ex-vessel prices reported by dealers in the MAB
region, NMFS estimated the potential change in fishery revenues from
the mainline length restriction, depending on the level of compensation
in fishing effort, to range from an increase of $777,747 (full
compensation in the number of hooks fished) to a loss of $819,523 (no
compensation in the number of hooks fished), with an estimated loss of
$239,383 with 50 percent compensation in the number of hooks fished.
This change in revenues would impact 41 or fewer vessels per year based
on current trends in the number of active pelagic longline vessels and
the number of vessels that operated in the MAB in 2006. If one assumes
that 41 vessels are affected by this restriction, then the estimated
annual impact per vessel ranges from an increase of $18,969 per vessel
to a decrease of $19,988 per vessel, with an estimated decrease of
$5,838 under the most likely scenarios (50 percent compensation in
fishing effort).
The economic costs of Alternative 4 were evaluated based upon
historical observed catch rates and reported effort in the MAB fishing
area only for the period 2002 to 2004. The impact of the closure of the
southern region of the MAB from July-December was estimated by assuming
no catch in that area, resulting in a total estimated cost of $770,000.
The combined effect of the 6-month closure and the mainline length
[[Page 35630]]
restriction through the MAB resulted in an estimated cost of $1.64
million, reflecting only lost catch and assuming no compensation or
redistribution of effort. The reduction in revenues would impact 41 or
fewer vessels per year based on the current trends in the number of
active pelagic longline vessels and the number of vessels that operated
in the MAB in 2006. If one assumes that 41 vessels would be affected by
this restriction, then per vessel impacts are estimated to be $40,000.
Alternative 1 (the no action alternative) and Alternative 2 were
not selected because they were not expected to meet the conservation
objectives of the proposed rule or the goals in MMPA section 118. Both
Alternative 3 and Alternative 4 would meet the objectives of the
proposed rule. Alternative 4 was not selected because, although it
would meet objectives of the proposed rule, it would likely result in
larger economic impacts to small entities than the preferred
alternative.
References Cited
A complete list of all references cited in this proposed rule can
be found on the PLTRT website at https://www.nmfs.noaa.gov/pr/
interactions/trt/teams.htm#pl-trt.htm and the NMFS Southeast Regional
Office website at https://sero.nmfs.noaa.gov/pr/pr.htm, and is available
upon request from the NMFS Southeast Regional Office in St. Petersburg,
FL (see ADDRESSES).
List of Subjects in 50 CFR Part 229
Administrative practice and procedure, Fisheries, Reporting and
recordkeeping requirements.
Dated: June 18, 2008.
John Oliver,
Deputy Assistant Administrator for Operations, National Marine
Fisheries Service.
For the reasons set out in the preamble, 50 CFR part 229 is
proposed to be amended as follows:
PART 229--AUTHORIZATION FOR COMMERCIAL FISHERIES UNDER THE MARINE
MAMMAL PROTECTION ACT OF 1972
1. The authority citation for part 229 continues to read as
follows:
Authority: 16 U.S.C. 1361 et seq.
2. In subpart A, Sec. 229.3, paragraphs (t) and (u) are added to
read as follows:
Sec. 229.3 Prohibitions.
* * * * *
(t) It is prohibited to deploy or fish with pelagic longline gear
in the Mid-Atlantic Bight unless the vessel:
(1) Complies with the placard posting requirement specified in
Sec. 229.36(c); and
(2) Complies with the gear restrictions specified in Sec.
229.36(e).
(u) It is prohibited to deploy or fish with pelagic longline gear
in the CHSRA or to transit through the CHSRA with pelagic longline gear
onboard unless the vessel is in compliance with the observer and
research requirements specified in Sec. 229.36(d).
3. In subpart C, Sec. 229.36 is added to read as follows:
Sec. 229.36 Atlantic Pelagic Longline Take Reduction Plan (PLTRP).
(a) Purpose and scope. The purpose of this section is to implement
the PLTRP to reduce incidental mortality and serious injury of long-
finned and short-finned pilot whales and Risso's dolphins in the
Atlantic pelagic longline fishery off the U.S. east coast, a component
of the Atlantic Ocean, Caribbean, Gulf of Mexico large pelagics
longline fishery, as delineated on the MMPA List of Fisheries.
(1) Persons subject to this section. The regulations in this
section apply to the owner and operator of any vessel that has been
issued or is required to be issued an Atlantic HMS tunas, swordfish, or
shark permit under Sec. 635.4 or Sec. 635.32 and that has pelagic
longline gear onboard as defined under Sec. 635.21(c).
(2) Geographic scope. The geographic scope of the PLTRP is the
Atlantic federal EEZ off the U.S. East Coast. The regulations specified
in paragraphs (b) through (e) of this section apply to all U.S.
Atlantic pelagic longline vessels operating in the EEZ portion of the
Mid-Atlantic Bight.
(b) Definitions. In addition to the definitions contained in the
MMPA and Sec. Sec. 216.3 and 229.2 of this chapter, the following
definitions apply.
(1) CHSRA (Cape Hatteras Special Research Area) means all waters
inside and including the rectangular boundary described by the
following lines: 35[deg] N. lat., 75[deg] W. long., 36[deg] 25' N.
lat., and 74[deg] 35' W. long.
(2) Mid-Atlantic Bight means the area bounded by straight lines
connecting the mid-Atlantic states' internal waters and extending to
71[deg] W. long. between 35[deg] N. lat. and 43[deg] N. lat.
(3) Observer means an individual authorized by NMFS, or a
designated contractor, placed aboard a commercial fishing vessel, to
record information on marine mammal interactions, fishing operations,
marine mammal life history information, and other scientific data; to
collect biological specimens; and to perform other scientific
investigations.
(4) Pelagic longline has the same meaning as in Sec. 635.2 of this
title.
(c) Marine Mammal Handling and Release Placard. The placard,
``Marine Mammal Handling/Release Guidelines: A Quick Reference for
Atlantic Pelagic Longline Gear,'' must be kept posted inside the
wheelhouse and on the working deck. You may contact the NMFS Southeast
Regional Office at (727) 824-5312 to request additional copies of the
placard.
(d) CHSRA--(1) Special observer requirements. If you deploy or fish
with pelagic longline gear in the CHSRA or transit through the CHSRA
with pelagic longline gear onboard, or intend to do so, you must call
NMFS Southeast Fisheries Science Center, 1-800-858-0624, at least 48
hours prior to embarking on your trip. This requirement is in addition
to any existing selection and notification requirement for observer
coverage by the Pelagic Observer Program. If you are assigned an
observer, you must take the observer during that trip. If you do not
take the observer, you are prohibited from deploying or fishing with
pelagic longline gear in the CHSRA or transiting through the CHSRA with
pelagic longline gear onboard. You must comply with all provisions of
Sec. 229.7, Monitoring of incidental mortalities and serious injuries.
In addition, all provisions of Sec. 600.746, Observers, apply. No
waivers will be granted under Sec. 229.7(c)(3) or Sec. 600.746(f). A
vessel that would otherwise be required to carry an observer, but is
inadequate or unsafe for purposes of carrying an observer and for
allowing operation of normal observer functions, is prohibited from
deploying or fishing with pelagic longline gear in the CHSRA or
transiting through the CHSRA with pelagic longline gear onboard.
(2) Special research requirements. In addition to observing normal
fishing activities, observers may conduct additional scientific
investigations aboard your vessel designed to support the goals of the
PLTRP. The observer will inform you of the specific additional
investigations that may be conducted during your trip. An observer may
direct you to modify your fishing behavior, gear, or both. Instead of
carrying an observer, you may be required to carry and deploy gear
provided by NMFS or an observer or modify your fishing practices. By
calling in per Sec. 229.36(d)(1), you are agreeing to take an
observer. You are also acknowledging you are both willing and able to
participate in research, as per this paragraph, in the CHSRA consistent
with the PLTRP without any compensation. If you are assigned any
[[Page 35631]]
special research requirements, you must participate in the research for
the duration of the assignment. If you do not participate in the
research, you are prohibited from deploying or fishing with pelagic
longline gear in the CHSRA or transiting through the CHSRA with pelagic
longline gear onboard.
(e) Gear restrictions. No person may deploy a pelagic longline that
exceeds 20 nautical miles (nm) (37.04 km) in length in the Mid-Atlantic
Bight, including in the CHSRA, unless they have a written letter of
authorization from the Director, NMFS Southeast Fishery Science Center
to use a pelagic longline exceeding 20 nm in the CHSRA in support
research for reducing bycatch of marine mammals in the pelagic longline
fishery.
[FR Doc. E8-14274 Filed 6-23-08; 8:45 am]
BILLING CODE 3510-22-S